145
INORGANIC AND ORGANIC LEAD COMPOUNDS Metallic lead and several inorganic and organic lead compounds have been considered by previous working groups convened by IARC (IARC, 1972, 1973, 1976, 1980, 1987). New data have since become available, and these are included in the present monograph and have been taken into consideration in the evaluation. The agents considered in this monograph are some inorganic and organic lead compounds. 1. Exposure Data 1.1 Chemical and physical data 1.1.1 Nomenclature, synonyms, trade names, molecular formulae, chemical and physical properties Synonyms, trade names and molecular formulae for lead and some inorganic and organic lead compounds are presented in Table 1. The lead compounds shown are those for which data on carcinogenicity or mutagenicity are available or which are commercially most important. The list is not exhaustive. Selected chemical and physical properties of the lead compounds listed in Table 1 are presented in Table 2. Lead (atomic number, 82; relative atomic mass, 207.2) has a valence +2 or +4. The alchemists believed lead to be the oldest metal and associated it with the planet Saturn. Lead is a bluish-white metal of bright lustre, is very soft, highly malleable, ductile and a poor conductor of electricity. It is very resistant to corrosion; lead pipes bearing the insignia of Roman emperors, used as drains from the baths, are still in service (Lide, 2003). Natural lead is a mixture of four stable isotopes: 204 Pb (1.4%), 206 Pb (25.2%), 207 Pb (21.7%) and 208 Pb (51.7%) (O’Neil, 2003). Lead isotopes are the end-products of each of the three series of naturally occurring radioactive elements: 206 Pb for the uranium series, 207 Pb for the acti- nium series and 208 Pb for the thorium series. Forty-three other isotopes of lead, all of which are radioactive, are recognized (Lide, 2003). 39

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  • INORGANIC AND ORGANIC LEAD COMPOUNDS

    Metallic lead and several inorganic and organic lead compounds have been considered

    by previous working groups convened by IARC (IARC, 1972, 1973, 1976, 1980, 1987).

    New data have since become available, and these are included in the present monograph

    and have been taken into consideration in the evaluation. The agents considered in this

    monograph are some inorganic and organic lead compounds.

    1. Exposure Data

    1.1 Chemical and physical data

    1.1.1 Nomenclature, synonyms, trade names, molecular formulae, chemical andphysical properties

    Synonyms, trade names and molecular formulae for lead and some inorganic and

    organic lead compounds are presented in Table 1. The lead compounds shown are those for

    which data on carcinogenicity or mutagenicity are available or which are commercially

    most important. The list is not exhaustive.

    Selected chemical and physical properties of the lead compounds listed in Table 1 are

    presented in Table 2.

    Lead (atomic number, 82; relative atomic mass, 207.2) has a valence +2 or +4. The

    alchemists believed lead to be the oldest metal and associated it with the planet Saturn.

    Lead is a bluish-white metal of bright lustre, is very soft, highly malleable, ductile and a

    poor conductor of electricity. It is very resistant to corrosion; lead pipes bearing the insignia

    of Roman emperors, used as drains from the baths, are still in service (Lide, 2003). Natural

    lead is a mixture of four stable isotopes: 204Pb (1.4%), 206Pb (25.2%), 207Pb (21.7%) and208Pb (51.7%) (O’Neil, 2003). Lead isotopes are the end-products of each of the three series

    of naturally occurring radioactive elements: 206Pb for the uranium series, 207Pb for the acti-

    nium series and 208Pb for the thorium series. Forty-three other isotopes of lead, all of which

    are radioactive, are recognized (Lide, 2003).

    –39–

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    740Table 1. Synonyms and trade names, registry numbers, molecular formulae, and molecular weights for lead and lead

    compounds

    Chemical name Synonyms and trade names (Chemical Abstracts Service name in italics) CAS registry

    numbera

    Molecular formula Molecular

    weightb

    Calcium plumbate Pigment Brown 10 12013-69-3 Ca2PbO4 [351.4]

    Lead, lead powder C.I. 77575; C.I. Pigment Metal 4; Lead element; Lead Flake; Lead S 2;

    Pb-S 100; SSO 1

    7439-92-1 Pbc 207.2

    c

    Lead acetate Acetic acid, lead(2+) salt; acetic acid lead salt (2:1); dibasic lead acetate; lead bis(acetate); lead diacetate; lead dibasic acetate; lead(2+)

    acetate; lead(II) acetate; neutral lead acetate; normal lead acetate;

    plumbous acetate; salt of Saturn; sugar of lead

    301-04-2 Pb(C2H3O2)2 325.3

    Lead acetate

    trihydrate

    Acetic acid, lead(2+) salt, trihydrate; lead diacetate trihydrate; lead(II) acetate trihydrate; plumbous acetate trihydrate; sugar of lead

    6080-56-4 Pb(C2H3O2)2·3H2O 379.3

    Lead arsenate Arsenic acid (H3AsO4), lead(2+) salt (2:3); lead(2+) orthoarsenate (Pb3(AsO4)2); Nu Rexform; trilead diarsenate

    3687-31-8 Pb3(AsO4)2 899.4

    Lead azide Lead azide (Pb(N3)2); lead azide (PbN6); lead diazide; lead(2+) azide; RD 1333

    13424-46-9

    [85941-57-7]

    Pb(N3)2 291.2

    Lead bromide Lead bromide (PbBr2); lead dibromide 10031-22-8 PbBr2 367.0

    Lead carbonate Carbonic acid, lead(2+) salt (1:1); lead carbonate (PbCO3); basic lead carbonate; dibasic lead carbonate; lead(2+) carbonate; plumbous

    carbonate; cerussite; white lead

    598-63-0 PbCO3 267.2

    Lead chloride Lead chloride (PbCl2); lead dichloride; lead(2+) chloride; lead(II) chloride; plumbous chloride; natural cotunite

    7758-95-4 PbCl2 278.1

    Lead chromate Chromic acid (H2CrO4), lead(2+) salt (1:1); lead chromate(VI); lead chromate (PbCrO4); lead chromium oxide (PbCrO4); plumbous

    chromate; Royal Yellow 6000; chrome yellow

    7758-97-6

    [8049-64-7]

    PbCrO4 323.2

    Lead fluoride Lead fluoride (PbF2); lead difluoride; lead difluoride (PbF2); lead(2+) fluoride; plumbous fluoride

    7783-46-2

    [106496-44-0]

    PbF2 245.2

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    Table 1 (contd)

    Chemical name Synonyms and trade names (Chemical Abstracts Service name in italics) CAS registry

    numbera

    Molecular formula Molecular

    weightb

    Lead fluoroborate Borate(1-), tetrafluoro-, lead(2+) salt (2:1); borate(1-), tetrafluoro-,

    lead(2+); lead fluoborate; lead tetrafluoroborate; lead boron fluoride;

    lead fluoroborate (Pb(BF4)2); lead(II) tetrafluoroborate

    13814-96-5

    [35254-34-3]

    Pb(BF4)2 380.8

    Lead hydrogen

    arsenate

    Arsenic acid (H3AsO4), lead(2+) salt (1:1); lead arsenate (PbHAsO4); acid lead arsenate; arsenic acid lead salt; lead acid arsenate; lead

    arsenate; lead hydrogen arsenate (PbHAsO4); lead(2+) monohydrogen

    arsenate

    7784-40-9

    [14034-76-5;

    37196-28-4]

    PbHAsO4 347.1

    Lead iodide Lead iodide (PbI2); C.I. 77613; lead diiodide; lead(II) iodide; plumbous iodide

    10101-63-0

    [82669-93-0]

    PbI2 461.0

    Lead naphthenate Naphthenic acids, lead salts; lead naphthenates; naphthenic acid, lead salt; Naphthex Pb; Trokyd Lead

    61790-14-5 Unspecified

    Lead nitrate Nitric acid, lead(2+) salt; lead dinitrate; lead nitrate (Pb(NO3)2); lead(2+) bis(nitrate); lead(2+) nitrate; lead(II) nitrate; plumbous nitrate

    10099-74-8

    [18256-98-9]

    Pb(NO3)2 331.2

    Lead dioxide Lead oxide (PbO2); C.I. 77580; lead brown; lead oxide brown; lead peroxide; lead superoxide; lead(IV) oxide; plumbic oxide; Thiolead A

    1309-60-0

    [60525-54-4]

    PbO2 239.2

    Lead monoxide Lead oxide (PbO); C.I. 77577; C.I. Pigment Yellow 46; lead monooxide; lead oxide yellow; lead protoxide; lead(2+) oxide; lead(II) oxide; litharge; Litharge S; Litharge Yellow L-28; plumbous oxide;

    yellow lead ochre

    1317-36-8

    [1309-59-7;

    12359-23-8]

    PbO 223.2

    Lead trioxide Lead trioxide (Pb2O3); C.I. 77579; lead sesquioxide; lead sesquioxide (Pb2O3); plumbous plumbate

    1314-27-8 Pb2O3 462.4

    Lead phosphate Phosphoric acid, lead(2+) salt (2:3); lead phosphate (Pb3P2O8); C.I. 77622; C.I. Pigment White 30; lead diphosphate; lead orthophosphate; lead phosphate (3:2); lead(2+) phosphate (Pb3(PO4)2); lead(II) phosphate

    (3:2); Perlex Paste 500; Perlex Paste 600A; Trilead phosphate; lead

    phosphate dibasic

    7446-27-7 Pb3(PO4)2 811.5

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    742

    Table 1 (contd)

    Chemical name Synonyms and trade names (Chemical Abstracts Service name in italics) CAS registry

    numbera

    Molecular formula Molecular

    weightb

    Lead phosphite,

    dibasic

    Dibasic lead phosphite; lead dibasic phosphite; dibasic lead

    metaphosphate; C.I. 77620; lead oxide phosphonate, hemihydrate

    1344-40-7 2PbO·PbHPO3·1/2H2O [743]

    Lead molybdate Lead molybdate(VI); lead molybdate oxide (PbMoO4) 10190-55-3 PbMoO4 367.1

    Lead stearate Octadecanoic acid, lead(2+) salt; 5002G; lead distearate; lead(2+) octadecanoate; lead(2+) stearate; lead(II) octadecanoate; lead(II)

    stearate; Listab 28ND; Pbst; SL 1000 (stabilizer); SLG; Stabinex NC18;

    stearic acid, lead(2+) salt

    1072-35-1

    [11097-78-2;

    37223-82-8]

    Pb(C18H35O2)2 774.1

    Lead stearate,

    dibasic

    Dibasic lead stearate; Listab 51; lead, bis(octadecanoato)dioxodi-;

    stearic acid, lead salt, dibasic

    56189-09-4 2PbO·Pb(C17H35COO)2 1220

    Lead styphnate 1,3-Benzenediol, 2,4,6-trinitro-, lead(2+) salt (1:1); 2,4-dioxa-3-plumbabicyclo[3.3.1]nona-1(9),5,7-triene, 3,3-didehydro-6,8,9-trinitro-;

    lead, [styphnato(2-)]-; lead tricinate; lead trinitroresorcinate; Tricinat;

    2,4,6-trinitroresorcinol, lead(2+) salt (1:1)

    15245-44-0

    [4219-19-6;

    6594-85-0;

    59286-40-7;

    63918-97-8]

    Pb(C6H3N3O8) [452.3]

    Lead subacetate Lead, bis(acetato-êO)tetrahydroxytri-; lead acetate (Pb3(AcO)2(OH)4); lead, bis(acetato)-tetrahydroxytri-; lead, bis(acetato-O)tetra-hydroxytri-;

    bis(acetato)dihydroxytrilead; lead acetate hydroxide (Pb3(OAc)2(OH)4);

    lead acetate, basic; monobasic lead acetate

    1335-32-6 Pb(CH3COO)2·2Pb(OH)2 807.7

    Lead sulfate Sulfuric acid, lead(2+) salt (1:1); Anglislite; C.I. 77630; C.I. Pigment White 3; Fast White; Freemans White Lead; HB 2000; Lead Bottoms;

    lead monosulfate; lead(II) sulfate (1:1); lead(2+) sulfate; lead(II) sulfate;

    Milk White; Mulhouse White; TS 100; TS 100 (sulfate); TS-E;

    sublimed white lead

    7446-14-2

    [37251-28-8]

    PbSO4 303.3

    Lead sulfide Lead sulfide (PbS); C.I. 77640; lead monosulfide; lead sulfide (1:1); lead(2+) sulfide; lead(II) sulfide; natural lead sulfide; P 128; P 37;

    plumbous sulfide

    1314-87-0

    [51682-73-6]

    PbS 239.3

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    Table 1 (contd)

    Chemical name Synonyms and trade names (Chemical Abstracts Service name in italics) CAS registry

    numbera

    Molecular formula Molecular

    weightb

    Lead tetraoxide Lead oxide (Pb3O4); Azarcon; C.I. 77578; C.I. Pigment Red 105; Entan; Gold Satinobre; Heuconin 5; lead orthoplumbate; lead oxide (3:4); lead oxide red; lead tetroxide; Mennige; Mineral Orange; Mineral red; Minium; Minium Non-Setting RL 95; Minium red; Orange Lead; Paris

    Red; red lead; red lead oxide; Sandix; Saturn Red; trilead tetraoxide; trilead tetroxide; plumboplumbic oxide

    1314-41-6

    [12684-34-3]

    Pb3O4 685.6

    Lead thiocyanate Thiocyanic acid, lead(2+) salt; lead bis(thiocyanate); lead dithiocyanate;

    lead(2+) thiocyanate; lead(II) thiocyanate

    592-87-0

    [10382-36-2]

    Pb(SCN)2 323.4

    Tetraethyl lead Plumbane, tetraethyl-; lead, tetraethyl-; TEL; tetraethyllead; tetraethylplumbane

    78-00-2 Pb(C2H5)4 323.5

    Tetramethyl lead Plumbane, tetramethyl-; lead, tetramethyl-; tetramethyllead; tetramethylplumbane; TML

    75-74-1 Pb(CH3)4 267.3

    From IARC (1980); Lide (2003); National Library of Medicine (2003); O’Neil (2003); STN International (2003) a Deleted Chemical Abstracts Service numbers shown in square brackets

    b Values in square brackets were calculated from the molecular formula.

    c Atomic formula; atomic weight

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    744

    Table 2. Physical and chemical properties of lead and lead compounds

    Chemical name Physical form Melting-point (°C) Boiling-point

    (°C)

    Density

    (g/cm3)

    Solubility (per 100 g H2O)

    Lead, lead powder Soft silvery-gray metal; cubic 327.5 1749 11.3 Insol. in water; sol. in conc. acid

    Lead acetate White crystal 280 Dec. 3.25 44.3 g at 20 °C; sl. sol. in

    ethanol

    Lead acetate trihydrate Colourless crystal 75 (dec) – 2.55 45.6 g at 15 °C; sl. sol. in

    ethanol

    Lead arsenate White crystal 1042 (dec) – 5.8 Insol. in water; sol. in nitric acid

    Lead azide Colourless orthorhombic needle ~350 (expl) – 4.7 23 mg at 18 °C; v. sol. in acetic

    acid

    Lead bromide White orthorhombic crystal 371 892 6.69 975 mg at 25 °C; insol. in

    ethanol

    Lead carbonate Colourless orthorhombic crystal ~315 (dec) – 6.6 Insol. in water; sol. in acid and

    alkaline solutions

    Lead chloride White orthorhombic needle or

    powder

    501 951 5.98 1.08 g at 25 °C; sol. in alkaline

    solutions; insol. in ethanol

    Lead chromate Yellow-orange monoclinic

    crystals

    844 – 6.12 17 µg at 20 °C; sol. in dilute acids

    Lead fluoride White orthorhombic crystal 830 1293 8.44 67 mg at 25 °C

    Lead fluoroborate Stable only in aqueous solution – – – Sol. in water

    Lead hydrogen arsenate White monoclinic crystal 280 (dec) 5.94 Insol. in water; sol. in nitric acid

    and alkaline solutions

    Lead iodide Yellow hexagonal crystal or

    powder

    410 872 (dec) 6.16 76 mg at 25 °C; insol. in ethanol

    Lead molybdate Yellow tertiary crystal ∼1060 – 6.7 Insol. in water; sol. in nitric acid and sodium hydroxide

    Lead naphthenate No data available

    Lead nitrate Colourless cubic crystal 470 – 4.53 59.7 g at 25 °C; sl. sol. in

    ethanol

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    Table 2 (contd)

    Chemical name Physical form Melting-point (°C) Boiling-point

    (°C)

    Density

    (g/cm3)

    Solubility (per 100 g H2O)

    Lead monoxide (PbO);

    litharge

    Red tetrahedral crystal Transforms to

    massicot at 489 °C

    – 9.35 Insol. in water and ethanol; sol.

    in dilute nitric acid

    Massicot Yellow orthorhombic crystal 897 – 9.64 Insol. in water and ethanol; sol.

    in dilute nitric acid

    Lead trioxide (Pb2O3) Black monoclinic crystal or red

    amorphous powder

    530 (dec) – 10.05 Insol. in water; sol. in alkaline

    solutions

    Lead phosphate White hexagonal crystal 1014 – 7.01 Insol. in water and ethanol; sol.

    in alkali and nitric acid

    Lead phosphite, dibasic Pale yellow powder 6.1

    Lead stearate White powder ~100 – 1.4 Insol. in water; sol. in hot

    ethanol

    Lead styphnate No data available

    Lead subacetate White powder Dec. – – 6.3 g at 0 °C; 25 g at 100 °C Lead sulfate Orthorhombic crystal 1087 – 6.29 4.4 mg at 25 °C; sl. sol. in

    alkaline solutions; insol. in acids

    Lead sulfide Black powder or silvery cubic

    crystal

    1113 – 7.60 Insol. in water; sol. in acids

    Lead tetraoxide Red tetrahedral crystals 830 – 8.92 Insol. in water and ethanol; sol.

    in hot hydrochloric acid

    Lead thiocyanate White to yellowish powder – – 3.82 50 mg at 20 °C

    Tetraethyl lead Liquid –136 200 (dec) 1.653 at

    20 °C

    Insol. in water; sol. in benzene;

    sl. sol. in ethanol and diethyl

    ether

    Tetramethyl lead Liquid –30.2 110 1.995 at

    20 °C

    Insol. in water; sol. in benzene,

    ethanol and diethyl ether

    From IARC (1980); Lide (2003); Physical and Theoretical Chemistry Laboratory (2004)

    Abbreviations: conc., concentrated; insol., insoluble; sl. sol., slightly soluble; sol., soluble; v. sol., very soluble; dec, decomposes; expl., explodes

    P 039-074 DEF.qxp 09/08/2006 11:04 Page 45

  • 1.1.2 Technical products and impurities

    Lead is produced in purity greater than 99.97% in many countries. Lead oxides and

    mixtures of lead and lead oxides are also widely available. Tables 3 and 4 show the

    specifications for metallic lead and some lead compounds, respectively, from selected

    countries.

    IARC MONOGRAPHS VOLUME 8746

    Table 3. Specifications for metallic lead from selected countries

    Country % Pb (min.) Contaminants with limits (% max.a) Reference

    Argentina 99.97 Fe, 0.002; Sb, 0.004; Zn, 0.001; Cu, 0.002;

    Ag, 0.0095; Bi, 0.035; Cd, 0.001; Ni, 0.001

    Industrias Deriplom

    SA (2003)

    Australia 99.97–99.99 Ag, 0.001; As, 0.001; Bi, 0.005–0.029; Cu,

    0.001; Sb, 0.001; Zn, 0.001; Cd, 0.001

    Pasminco Metals

    (1998)

    Belgium 99.9–99.95 (ppm) Bi, 90–250; Ag, 10–15; Cu, 5–10;

    As, 5; Sb, 3; Sn, 3; As+Sb+Sn, 8; Zn, 3–5;

    Fe, 3; Cd, 3–10; Ni, 2–3

    Umicore Precious

    Metals (2002)

    Bulgaria 99.97–99.99 Ag, 0.001–0.005; Cu, 0.0005–0.003; Zn,

    0.0002–0.0015; Fe, 0.001; Cd, 0.0002–

    0.001; Ni, 0.0005–0.001; As, 0.0005–0.002;

    Sb, 0.0005–0.005; Sn, 0.0005–0.001; Bi,

    0.005–0.03

    KCM SA (2003)

    Canada 99.97–99.99 NR Noranda (2003);

    Teck Cominco

    (2003)

    Kazakhstan 99.95–99.9996 NR Southpolymetal

    (2003)

    Mexico 99.97–99.99 Ag, 0.0015; Cu, 0.0005; Zn, 0.0005; Fe,

    0.0010; Bi, 0.0250; Sb, 0.0005; As, 0.0005;

    Sn, 0.0005; Ni, 0.0002; Te, 0.0001

    Penoles (2003)

    Republic

    of Korea

    99.995 Ag, 0.0003; Cu, 0.0003; As, 0.0003; Sb,

    0.0003; Zn, 0.0003; Fe, 0.0003; Bi, 0.0015;

    Sn, 0.0003

    Korea Zinc Co.

    (2003)

    USA 99.995–

    99.9999

    (ppm) Sb, 1; As, 1–5; Bi, 0.2–4; Cu, 1–4;

    Ag, < 0.1–2; Tl, 1–2; Sn, 0.3–1; Fe, < 0.1–

    0.3; Ca, 0.1–0.4; Mg, 0.1–0.3

    ESPI Corp. (2002)

    NR, not reported a Unless otherwise specified

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    Table 4. Specifications for some lead compounds from selected countries

    Country Compound Contaminants with limits (% max.) Gradea Reference

    Argentina Lead oxide Fe, 0.003; Sb, 0.001–0.004; Zn, 0.0005–

    0.001; Cu, 0.0005–0.002; Ag, 0.001–0.0095;

    Bi, 0.003–0.035; Cd, 0.0008–0.001; Ni,

    0.0008–0.001

    5 grades of red lead (Pb3O4 + PbO2 + PbO);

    3 grades of yellow litharge (PbO, 99.65–

    99.96%; free Pb, 0.03–0.30%; Pb3O4,

    0.0048–0.05%); 1 grade of green powder

    (PbO + Pb, 80%+20% or 62%+38%)

    Industrias

    Deriplom SA

    (2003)

    Australia Lead oxide Bi, 0.05–0.06; Ag, 0.001; Cu, 0.001; Sn,

    0.0005–0.001; Sb, 0.0001–0.0002; As,

    0.0001; Se, 0.0001; S, 0.0007; Cd, 0.0005;

    Ni, 0.0002–0.0003; Zn, 0.0005; Fe, 0.0002–

    0.0005; Mn, 0.0003–0.0005; Te, 0.00003–

    0.0001; Co, 0.0001–0.0002; Cr, 0.0002;

    Ba, 0.0005; V, 0.0004; Mo, 0.0003–0.0005

    VRLA-refinedTM and MF-refinedTM Pasminco

    Metals (2000)

    USA Lead acetate

    Lead bromide

    Lead chloride

    Lead fluoride

    Lead iodide

    Lead molybdate

    Lead monoxide

    Lead tetraoxide

    Lead sulfide

    NR 5N

    3N and 5N

    3N and 5N

    3N

    3N and 5N

    3N

    3N and 5N

    3N

    3N and 5N

    ESPI Corp.

    (2002)

    VRLA, valve-regulated lead acid; MF, maintenance-free; NR, not reported a 3N, 99.9%; 5N, 99.999%

    P 039-074 DEF.qxp 09/08/2006 11:04 Page 47

  • 1.2 Production

    Commercial lead metal is described as being either primary or secondary. Primary

    lead is produced directly from mined lead ore. Secondary lead is produced from scrap lead

    products which have been recycled.

    1.2.1 The ores and their preparation

    The most important lead ore is galena (lead sulfide). Other important ores such ascerussite (lead carbonate) and anglesite (lead sulfate) may be regarded as weatheredproducts of galena and are usually found nearer to the surface of the earth’s crust. Leadand zinc ores often occur together and, in most extraction methods, have to be separated.

    The most common separation technique is selective froth flotation. The ore is first

    processed to a fine suspension in water by grinding in ball or rod mills — preferably to a

    particle size of < 0.25 mm. Air is then bubbled through this pulp contained in a cell or tank

    and, following the addition of various chemicals and proper agitation, the required

    mineral particles become attached to the air bubbles and are carried to the surface to form

    a stable mineral-containing froth which is skimmed off. The unwanted or gangue particles

    are unaffected and remain in the pulp. For example, with lead–zinc sulfide ores, zinc

    sulfate, sodium cyanide or sodium sulfite can be used to depress the zinc sulfide, while

    the lead sulfide is floated off to form a concentrate. The zinc sulfide is then activated by

    copper sulfate and floated off as a second concentrate (Lead Development Association

    International, 2003a).

    Around 3 million tonnes of lead are mined in the world each year. Lead is found all

    over the world but the countries with the largest mines are Australia, China and the United

    States of America, which together account for more than 50% of primary production. The

    most common lead ore is galena (lead sulfide). Other elements frequently associated withlead include zinc and silver. In fact, lead ores constitute the main sources of silver, contri-

    buting substantially towards the world’s total silver output (Lead Development

    Association International, 2003b). Table 5 shows mine production of lead concentrate by

    country in the year 2000. Table 6 shows the trends in lead mine production by geographic

    region from 1960 to 2003.

    1.2.2 Smelting

    (a) Two-stage processesThe first stage in smelting consists of removing most of the sulfur from the lead con-

    centrate. This is achieved by a continuous roasting process (sintering) in which the lead

    sulfide is largely converted to lead oxide and broken down to a size convenient for use in

    a blast furnace — the next stage in the process. The sinter plant gases containing sulfur

    are converted to sulfuric acid (Lead Development Association International, 2003a).

    IARC MONOGRAPHS VOLUME 8748

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  • The graded sinter (lead oxide) is mixed with coke and flux, such as limestone, and fed

    into the top of the blast furnace, where it is smelted using an air blast (sometimes pre-

    heated) introduced near the bottom. The chemical processes that take place in the furnace

    at about 1200 °C result in the production of lead bullion (lead containing only metallicimpurities) which is tapped off from the bottom of the furnace and either cast into ingots

    or collected molten in ladles for transfer to the refining process. In the Imperial Smelting

    Furnace process, a very similar procedure is used for the simultaneous production of zinc

    and lead.

    These traditional two-stage processes largely favour the release of hazardous dusts and

    fumes. They necessitate the use of extensive exhaust ventilation and result in large volumes

    INORGANIC AND ORGANIC LEAD COMPOUNDS 49

    Table 5. Mine production of lead concentrate in 2000a

    Country Production

    (tonnes)

    Country Production

    (tonnes)

    Algeria 818 Mexico 137 975

    Argentina 14 115 Morocco 81 208c

    Australia 739 000 Myanmar 1 200b

    Bolivia 9 523 Namibia 11 114c

    Bosnia and Herzegovina 200b Peru 270 576

    Brazil 8 832 Poland 51 200c

    Bulgaria 10 500 Republic of Korea 2 724

    Canada 152 765 Romania 18 750c

    Chile 785c Russian Federation 13 300

    China 660 000b Serbia and Montenegro 9 000

    Colombia 226 South Africa 75 262

    Democratic People’s 60 000b,c Spain 40 300

    Republic of Korea Sweden 106 584c

    Ecuador 200b Tajikistan 800b

    Georgia 200b Thailand 15 600

    Greece 18 235b The former Yugoslav 25 000b

    Honduras 4 805 Republic of Macedonia

    India 28 900 Tunisia 6 602

    Iran 15 000b Turkey 17 270

    Ireland 57 825 United Kingdom 1 000b

    Italy 2 000 USA 465 000

    Japan 8 835 Viet Nam 1 000b

    Kazakhstan 40 000 World totald 3 180 000c

    From Smith (2002)

    In addition to the countries listed, lead is also produced in Nigeria, but information is

    inadequate to estimate output. a Data available at 1 July 2003 b Estimated c Revised d Data from the USA and estimated data are rounded to no more than three significant

    digits, so that values may not add to total shown.

    P 039-074 DEF.qxp 09/08/2006 11:04 Page 49

  • of lead-laden exhaust gases which are usually cleaned before they are discharged into the

    atmosphere. The collected dusts are returned to the smelting process (Lead Development

    Association International, 2003a).

    (b) Direct smelting processesThe environmental problems and inefficient use of energy associated with the sinter/

    blast furnace and Imperial Smelting Furnace processes have led to a considerable amount

    of research into more economical and less polluting methods for the production of lead.

    Most of this research has been aimed at devising processes in which lead is converted

    directly from the sulfide to the metal without producing lead oxide. As a result, a number

    IARC MONOGRAPHS VOLUME 8750

    Table 6. Trends in lead mine production worldwide

    Production (thousand tonnes) by geographical regiona Year

    Ab B C Db E Fb Total

    1960 370 207 822 84 306 583 2372

    1965 366 250 984 99 361 724 2784

    1970 476 210 1341 120 441 855 3443

    1975 435 165 1340 140 395 1085 3560

    1980 482 278 1298 112 382 1030 3582

    1985 412 261 1197 155 474 1076 3575

    1990 727 175 1184 545 556 NRS 3187

    1995 382 186 1047 715 424 NRS 2753

    2000 360 178 1053 805 650 NRS 3046

    2003 218 123 1043 770 666 NRS 2821

    From International Lead and Zinc Study Group (1990, 2004)

    NRS, not reported separately a Data from following countries:

    A, Austria, Denmark, Finland, France, Germany (the Federal Republic of Germany before

    reunification), Greece, Ireland, Italy, Norway, Portugal, Spain, Sweden, United Kingdom and

    former Yugoslavia

    B, Algeria, Congo, Morocco, Namibia, South Africa, Tunisia and Zambia

    C, Argentina, Bolivia, Brazil, Canada, Chile, Colombia, Guatemala, Honduras, Mexico,

    Nicaragua, Peru and USA

    D, Myanmar, India, Iran, Japan, Philippines, Republic of Korea, Thailand and Turkey

    E, Australia

    F, Bulgaria, China, former Czechoslovakia, Hungary, People’s Democratic Republic of Korea,

    Poland, Romania and the former Soviet Union; values for the latter four countries are estimates. b From 1990 onwards, data from region F are included in region A (for Belarus, Bulgaria, Czech

    Republic, Estonia, Hungary, Latvia, Lithuania, Poland, Romania, the Russian Federation,

    Slovakia and Ukraine) or region D (for all former Soviet Republics, China and People’s Demo-

    cratic Republic of Korea); lead mine production for 1991 in the former Soviet Union is split as

    follows: Europe, 19%; Asia, 81%.

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  • of direct smelting processes now exist, although at varying stages of development (Lead

    Development Association International, 2003a).

    Direct smelting processes offer several significant advantages over conventional

    methods. The first and most obvious advantage is that sintering is no longer necessary. As

    a result, the creation of dust, a major occupational and environmental problem, is avoided.

    Moreover, the heat evolved during sintering (for the oxidation of the ore) is no longer

    wasted but is used in the smelting operation, thus providing a considerable saving of fuel.

    The volumes of gas that require filtering are largely reduced and, at the same time, the

    sulfur dioxide concentration of the off-gases is greater and these are therefore more

    suitable for the manufacture of sulfuric acid. The major difficulty in all direct smelting

    processes lies in obtaining both a lead bullion with an acceptably low sulfur content and

    a slag with a sufficiently low lead content for it to be safely and economically discarded.

    In several cases, further treatment of the crude bullion or the slag or both is required in a

    separate operation. There are several direct smelting processes which come close to

    meeting the desired criteria — the Russian Kivcet, the QSL (Queneau–Schuhmann–

    Lurgi), the Isasmelt and the Outokumpu processes are examples. The use of these newer

    processes will probably increase.

    At present, the relative importance of the different smelting methods in terms of

    amounts of metal produced is as follows: conventional blast furnace, 80%; Imperial

    Smelting Furnace process, 10%; and direct processes, 10% (Lead Development Asso-

    ciation International, 2003a).

    1.2.3 Hydrometallurgical processes

    With the prospect of even tighter environmental controls, the possibilities of utilizing

    hydrometallurgical techniques for the treatment of primary and secondary sources of lead

    are being investigated. Several processes have been described in the literature, but most

    are still in the developmental stage and probably not yet economically viable in compa-

    rison with the pyrometallurgical (smelting) processes. The goal of the hydrometallurgical

    processes in most cases is to fix the sulfur as a harmless sulfate and to put the lead into a

    solution suitable for electrolytic recovery. Most of these processes recirculate leach

    solutions and produce lead of high purity. For example, the Ledchlor process can be used

    on primary materials; other methods such as Rameshni SO2 Reduction (RSR) and the

    processes developed by Engitec (CX-EW) and Ginatta (Maja et al., 1989) are moreconcerned with recovery of lead from secondary sources, in particular from battery scrap

    (Lead Development Association International, 2003a).

    1.2.4 Primary lead refining

    Apart from gold and silver, lead bullion contains many other metallic impurities

    including antimony, arsenic, copper, tin and zinc. Copper is the first of the impurities to

    be removed. The lead bullion is melted at about 300–600 °C and held just above its

    INORGANIC AND ORGANIC LEAD COMPOUNDS 51

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  • melting-point when solid copper rises to the surface and is skimmed off. Sulfur is stirred

    into the melt to facilitate the operation by producing a dry powdery dross which is more

    readily removed. Once copper has been removed, there are a number of processes

    available for the extraction of the other impurities from the bullion. These include pyro-

    metallurgical techniques, in which elements are removed one or more at a time in several

    stages, and electrolytic processes that remove most of the impurities in one operation.

    Although electrolytic methods are used in large-scale production, pyrometallurgical

    techniques account for the larger portion of the world’s refined lead production (Lead

    Development Association International, 2003c). Table 7 shows the trends in production of

    refined lead by geographic region from 1960 to 2003.

    IARC MONOGRAPHS VOLUME 8752

    Table 7. Trends in refined lead production worldwide

    Production (thousand tonnes) by geographical regiona Year

    Ab B C Db E Fb Total

    1960 950 70 1114 164 211 718 3227

    1965 1046 124 1296 202 223 823 3714

    1970 1412 147 1619 301 217 992 4688

    1975 1354 124 1661 296 198 1195 4828

    1980 1514 156 1776 397 241 1331 5415

    1985 1613 159 1708 539 220 1416 5655

    1990 2323 150 1900 924 229 NRS 5525

    1995 1796 141 2102 1474 243 NRS 5756

    2000 1882 125 2216 2163 263 NRS 6650

    2003 1606 144 2043 2499 311 NRS 6603

    From International Lead and Zinc Study Group (1990, 2004)

    NRS, not reported separately

    a Data from the following countries:

    A, Austria, Belgium, Denmark, Finland, France, Germany (the Federal Republic of Germany

    before reunification), Greece, Ireland, Italy, Netherlands, Norway, Portugal, Spain, Sweden,

    Switzerland, United Kingdom and former Yugoslavia

    B, Algeria, Morocco, Namibia, South Africa, Tunisia and Zambia

    C, Argentina, Brazil, Canada, Mexico, Peru, USA and Venezuela

    D, Myanmar, India, Indonesia, Japan, Malaysia, Philippines, Republic of Korea, China (Province

    of Taiwan), Thailand, and Turkey

    E, Australia and New Zealand

    F, Bulgaria, China, former Czechoslovakia, Germany (former Democratic Republic of),

    Hungary, People’s Democratic Republic of Korea, Poland, Romania and former Soviet Union;

    values for Bulgaria, former German Democratic Republic, Romania, former Soviet Union, China

    and People’s Democratic Republic of Korea are estimates. b From 1990 onwards, data from region F are included in region A (Belarus, Bulgaria, Czech

    Republic, Estonia, Germany (former German Democratic Republic), Hungary, Latvia, Lithuania,

    Poland, Romania, Russian Federation and Ukraine) or in region D (China, all other former Soviet

    Republics and People’s Democratic Republic of Korea); refined lead production in the former

    Soviet Union for 1991 is split as follows: Europe, 24%; Asia, 76%.

    P 039-074 DEF.qxp 09/08/2006 11:04 Page 52

  • (a) Pyrometallurgical processes(i) Removal of antimony, arsenic and tin

    After the removal of copper, the next step is to remove antimony, arsenic and tin.

    There are two methods available — the softening process (so-called since these elements

    are standard hardeners for lead) and the Harris process. In the softening process, the lead

    bullion is melted and agitated with an air blast, causing preferential oxidation of the

    impurities which are then skimmed off as a molten slag. In the Harris process, the molten

    bullion is stirred with a flux of molten sodium hydroxide and sodium nitrate or another

    suitable oxidizing agent. The oxidized impurities are suspended in the alkali flux in the

    form of sodium antimonate, arsenate and stannate, and any zinc is removed in the form

    of zinc oxide (Lead Development Association International, 2003c).

    (ii) Removal of silver and goldAfter the removal of antimony, arsenic and tin, the softened lead may still contain

    silver and gold, and sometimes bismuth. The removal of the precious metals by the Parkes

    process is based on the fact that they are more soluble in zinc than in lead. In this process,

    the lead is melted and mixed with zinc at 480 °C. The temperature of the melt is graduallylowered to below 419.5 °C, at which point the zinc (now containing nearly all the silverand gold) begins to solidify as a crust on the surface of the lead and can be skimmed off.

    An alternative procedure, the Port Pirie process, used at the Port Pirie refinery in Australia,

    is based on similar metallurgical principles (Lead Development Association International,

    2003c).

    (iii) Removal of zincThe removal of the precious metals leaves zinc as the main contaminant of the lead.

    It is removed either by oxidation with gaseous chlorine or by vacuum distillation. The

    latter process involves melting the lead in a large kettle covered with a water-cooled lid

    under vacuum. The zinc distils from the lead under the combined influence of temperature

    and reduced pressure and condenses on the underside of the cold lid (Lead Development

    Association International, 2003c).

    (iv) Removal of bismuthAfter removal of zinc, the only remaining impurity is bismuth, although it is not

    always present in lead ore. It is easily removed by electrolysis and this accounts for the

    favouring of electrolytic methods in Canada (see below), where bismuth is a frequent

    impurity. When pyrometallurgical methods of refining are used, bismuth is removed by

    adding a calcium–magnesium alloy to the molten lead, causing a quaternary alloy of

    lead–calcium–magnesium–bismuth to rise to the top of the melt where it can be skimmed

    off (Lead Development Association International, 2003c).

    INORGANIC AND ORGANIC LEAD COMPOUNDS 53

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  • (b) Electrolytic processesIn the Betts process, massive cast anodes of lead bullion are used in a cell containing

    an electrolyte of acid lead fluorosilicate and thin cathode ‘starter sheets’ of high-purity lead.

    The lead deposited on the cathodes still contains tin and sometimes a small amount of

    antimony, and these impurities must be removed by melting and selective oxidation. For

    many years, the Betts process was the only process to remove bismuth efficiently. A more

    recent electrolytic process, first used in the 1950s in Italy, employs a sulfamate electrolyte.

    It is claimed to be an equally efficient refining method, with the advantage that the

    electrolyte is easier to prepare (Lead Development Association International, 2003c).

    By combining the processes described above to build up a complete refining scheme,

    it is possible to produce lead of very high purity. Most major refiners will supply bulk

    quantities of lead of 99.99% purity and, for very specific purposes, it is possible to reach

    99.9999% purity by additional processing (Lead Development Association International,

    2003c).

    1.2.5 Secondary lead production

    Much of the secondary lead comes from lead batteries, with the remainder originating

    from other sources such as lead pipe and sheet. Lead scrap from pipes and sheet is ‘clean’

    and can be melted and refined without the need for a smelting stage. With batteries, the lead

    can only be obtained by breaking the case open. This is commonly done using a battery

    breaking machine which, in addition to crushing the case, separates out the different com-

    ponents of the battery and collects them in hoppers. Thus, the pastes (oxide and sulfate),

    grids, separators and fragmented cases are all separated from one another. The battery acid

    is drained and neutralized, and the other components are either recycled or discarded (Lead

    Development Association International, 2003d).

    Table 8 shows trends in recovery of secondary lead by geographic region from 1970

    to 1988. Three million tonnes of lead are produced from secondary sources each year, by

    recycling scrap lead products. At least three-quarters of all lead is used in products which

    are suitable for recycling and hence lead has the highest recycling rate of all the common

    non-ferrous metals (Lead Development Association International, 2003a). Almost 50% of

    the 1.6 million tonnes of lead produced in Europe each year has been recycled. In the

    United Kingdom, the figure is nearer 60% (Lead Development Association International,

    2003d).

    (a) Secondary lead smeltingThe workhorse of the secondary lead production industry used to be the blast furnace.

    Conversion from blast to rotary-furnace technology in Europe began in the 1960s and was

    largely complete by the 1990s, driven by the high price of metallurgical coke and the

    relative difficulty of preventing the escape of dust and fume. The blast furnace was used to

    provide a low-grade antimonial lead, which was softened. The high-antimony slags were

    accumulated for a subsequent blast furnace campaign to produce a high-antimony bullion

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  • for blending into lead alloys. Although a few secondary smelters today still use furnaces

    based on blast furnace technology, most companies now use rotary furnaces in which the

    charge can be tailored to give a lead of approximately the desired composition. Alter-

    natively, a two-stage smelting procedure can be employed, which yields crude soft lead and

    crude antimonial lead. In the latter process, for example, battery plates are first melted and

    crude soft lead is tapped off after a few hours while the antimonial slag and lead oxide and

    sulfate are retained in the furnace. Further plates are charged and more soft lead is with-

    drawn until sufficient slag has accumulated for the slag reduction stage. Then, coke or

    anthracite fines and soda ash are added, lead and antimony oxides and lead sulfate are

    reduced and the cycle ends with the furnace being emptied of antimonial lead and of slag

    for discarding. As with primary smelting, large volumes of gas are produced, carrying

    substantial quantities of dust. On leaving the smelter, the gases are cooled from about

    900 °C to about 100 °C using air and/or water cooling, and pass into a baghouse where thedust is collected and eventually fed back into the smelter. The gases subsequently are

    released into the atmosphere. In the course of processing one tonne of lead, as much as 100

    tonnes of air have to be cleaned in this way (Lead Development Association International,

    2003d).

    In the semi-continuous Isasmelt furnace process used for secondary lead production,

    the furnace is fed with a lead carbonate paste containing 1% sulfur. This is obtained as a

    result of the battery paste having gone through a desulfurizing process after battery

    breaking. Over the following 36 h, wet lead carbonate paste and coal as a reductant are

    continuously fed into the furnace. The soft lead that is produced is tapped every 3 h and

    INORGANIC AND ORGANIC LEAD COMPOUNDS 55

    Table 8. Trends in recovery of secondary lead (refined lead and lead alloys produced from secondary materials)

    Recovery (thousand tonnes) by geographical regiona Year

    A B C D E Total

    1970 619 21 532 78 37 1287

    1975 617 29 610 115 39 1410

    1980 742 44 798 192 39 1815

    1985 766 44 747 258 20 1835

    1988 800 48 921 310 23 2102

    From International Lead and Zinc Study Group (1990) a Data from the following countries:

    A, Austria, Belgium, Denmark, Finland, France, Germany (the Federal Republic of

    Germany before reunification), Greece, Ireland, Italy, Netherlands, Portugal, Spain,

    Sweden, Switzerland, United Kingdom and former Yugoslavia

    B, Algeria, Morocco and South Africa

    C, Argentina, Brazil, Canada, Mexico, USA and Venezuela

    D, India, Japan and China (Province of Taiwan)

    E, Australia and New Zealand

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  • contains 99.9% lead. After 36 h, the paste feed is stopped and the slag is reduced to

    produce antimonial lead alloy. As with the two-stage process described above, off-gases

    from the furnace are first cooled and then passed into a baghouse for fume and dust

    control (Lead Development Association International, 2003d).

    (b) Secondary lead refiningThe principal impurities that are removed in secondary lead refining are copper, tin,

    antimony and arsenic. Zinc, iron, nickel, bismuth, silver and other impurities may also be

    present. These impurities are generally removed using the same basic techniques as

    described above (Lead Development Association International, 2003d).

    1.2.6 Lead production by compound and country

    Table 9 summarizes the available information on the number of companies in various

    countries producing metallic lead and some lead compounds in 2002.

    1.3 Use

    Over the centuries the unique properties of lead have resulted in its use in many

    different applications. These properties are mainly its high resistance to corrosion, its

    softness and low melting-point, its high density and its relatively low conductivity (Lead

    Development Association International, 2003b).

    Large quantities of lead, both as the metal and as the dioxide, are used in storage

    batteries. Lead is also used for cable covering, plumbing and ammunition. The metal is

    very effective as a sound absorber and as a radiation shield around X-ray equipment and

    nuclear reactors. It is also used to absorb vibration. Lead, alloyed with tin, is used in

    making organ pipes. Lead carbonate (PbCO3), lead sulfate (PbSO4), lead chromate

    (PbCrO4), lead tetraoxide (Pb3O4) and other lead compounds (see Table 1 for synonyms)

    have been applied extensively in paints, although in recent years this use has been curtailed

    to reduce health hazards. Lead oxide (usually lead monoxide) is used in the production of

    fine ‘crystal glass’ and ‘flint glass’ with a high index of refraction for achromatic lenses.

    Lead nitrate and acetate are soluble salts that serve as intermediates and in specialty

    applications. Lead salts such as lead arsenate have been used as insecticides, but in recent

    years this use has been almost eliminated (Lide, 2003).

    In most countries, lead is predominantly used as the metal and it may be alloyed with

    other materials depending on the application. Lead alloys are made by the controlled

    addition of other elements. The term ‘unalloyed lead’ implies that no alloying elements

    have been added intentionally; this may mean that the lead is of high purity, but the term

    also covers less pure lead containing incidental impurities (Lead Development Asso-

    ciation International, 2003e).

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  • INORGANIC AND ORGANIC LEAD COMPOUNDS 57

    Table 9. Lead production by compound and country

    Compound No. of

    companies

    Countries

    Metallic lead 10 Japan

    6 USA

    5 China, Mexico

    4 Belgium, Canada

    3 Brazil, Germany, Peru, Russian Federation

    2 Kazakhstan

    1 Argentina, Australia, Bolivia, Bulgaria, China (Province of

    Taiwan), Egypt, India, Ireland, Italy, Netherlands, Republic of

    Korea, Spain, Sweden, Turkey

    Lead acetate 10 China

    8 India

    7 Mexico

    6 USA

    5 Brazil, Japan

    3 Spain

    2 Germany, Italy

    1 Australia, China (Province of Taiwan), France, Romania, Russian

    Federation

    Lead arsenate 3 Japan

    1 Peru

    Lead azide 2 Brazil

    1 Japan

    Lead bromide 1 Germany, India, Japan, United Kingdom, USA

    6 India Lead carbonate

    2 China, China (Province of Taiwan), Germany, USA

    1 Argentina, Australia, Italy, Japan, Mexico, Republic of Korea,

    Romania, Ukraine and United Kingdom

    Lead chloride 5 India

    4 USA

    1 Australia, Belgium, China, China (Province of Taiwan),

    Germany, Japan, Mexico, Romania, Spain

    22 China

    8 India

    6 USA

    Lead chromate

    (Pigment

    Yellow 34)

    5 China (Province of Taiwan), Japan, Spain

    3 Germany, Italy

    2 Brazil, Republic of Korea, Netherlands, United Kingdom

    1 Argentina, Austria, Belgium, Canada, Colombia, France, Mexico,

    Peru, Romania, Russian Federation, Turkey, Venezuela

    Lead fluoride 4 China

    3 India, Japan, USA

    1 Argentina, Canada, France, Germany

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  • IARC MONOGRAPHS VOLUME 8758

    Table 9 (contd)

    Compound No. of

    companies

    Countries

    7 China, India Lead fluoroborate

    5 USA

    3 Japan

    2 Australia, China (Province of Taiwan), France, Germany

    1 Argentina, Brazil, Russian Federation, Spain

    Lead iodide 2 Japan, United Kingdom

    1 China, India, USA

    6 China Lead naphthenate

    5 Japan, Mexico

    3 Argentina, USA

    2 France, India, Peru, Spain

    1 Australia, Belgium, Brazil, Canada, China (Province of Taiwan),

    Germany, Italy, Romania, Thailand, Turkey

    Lead nitrate 12 India

    8 China

    7 USA

    6 Japan

    4 Brazil, Mexico

    3 Spain

    2 Belgium, Germany

    1 Australia, Italy, Russian Federation, Tajikistan

    24 China Lead monoxide

    7 Japan

    6 India

    4 China (Province of Taiwan), Germany, Mexico, USA

    3 France, Spain

    2 Brazil, Italy, Peru, Republic of Korea, Russian Federation

    1 Argentina, Australia, Canada, Kazakhstan, Malaysia, Portugal,

    South Africa, Tajikistan, Turkey, United Kingdom

    Lead dioxide 6 India

    4 Japan

    3 USA

    2 Germany

    1 Australia, Italy, South Africa, Spain, United Kingdom

    6 China Lead phosphate

    2 India

    1 Japan, Russian Federation

    Lead stearate 25 China

    17 India

    9 China (Province of Taiwan)

    4 Japan

    3 Germany, Spain, Thailand

    2 Mexico, Peru, Philippines, Republic of Korea, USA

    1 Albania, Argentina, Belgium, Brazil, Indonesia, Italy, Portugal,

    Romania, South Africa, Turkey

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  • INORGANIC AND ORGANIC LEAD COMPOUNDS 59

    Table 9 (contd)

    Compound No. of

    companies

    Countries

    15 India Lead stearate,

    dibasic 8 China

    5 China (Province of Taiwan)

    2 Japan, Philippines, Spain, Thailand, USA

    1 Belgium, Germany, Indonesia, Peru, Republic of Korea, South

    Africa, Turkey, United Kingdom

    Lead styphnate 2 Brazil

    1 Japan

    4 India Lead subacetate

    3 Mexico

    2 China

    1 Australia, Brazil, China (Province of Taiwan), Romania, Spain,

    USA

    Lead sulfate 6 India

    4 Mexico

    3 Germany

    2 Spain

    1 China, Japan, Romania, USA

    Lead sulfide 4 India

    2 France, Japan

    1 Austria, China, Germany, USA

    Lead tetraoxide 22 China

    5 India, Japan

    4 China (Province of Taiwan)

    3 Mexico, Spain

    2 Brazil, France, Germany, Italy, Russian Federation, USA

    1 Argentina, Kazakhstan, Peru, Poland, Portugal, Republic of

    Korea, South Africa, Tajikistan, Turkey, United Kingdom

    Lead thiocyanate 2 USA

    Lead trioxide 1 China

    Tetraethyl lead 1 Germany, Italy

    Tetramethyl lead 2 Russian Federation

    1 Italy

    From Chemical Information Services (2003)

    P 039-074 DEF.qxp 09/08/2006 11:04 Page 59

  • Trends in the reported consumption of lead by geographical region between 1960 and

    2003 are shown in Table 10. Tables 11 and 12 show the trends in total lead consumption

    by country and by major use category, respectively, in selected countries between 1985

    and 2001.

    For six of the major lead-consuming countries (France, Germany, Italy, Japan, the

    United Kingdom, USA), detailed historical data are available from 1960 to 1990 (Tables

    13–19). In this period, total consumption of lead reported by these countries rose from 2.06

    to 2.94 million tonnes, an overall increase of 43% and an average annual increase of 1.2%.

    During those three decades, however, there were marked changes in the rates of lead

    consumption. These included: (1) the rapid expansion of consumption during the 1960s

    and early 1970s leading to peak levels in 1973 prior to the onset of the first world energy

    crisis; (2) the steep reduction in 1974–75 and the subsequent revival in 1977–79, with lead

    consumption recovering to its 1973 level; (3) the decrease in 1980–82 during the second

    energy crisis; and (4) the sustained growth from 1983 until 1990 in the industrialized world

    as a whole, supported by rapid advances in some of the newly-industrializing countries, but

    with much more restricted progress in the fully-industrialized countries where the rates of

    economic expansion and industrial activity slowed down compared with those previously

    achieved (International Lead and Zinc Study Group, 1992).

    1.3.1 Lead–acid batteries

    By far the largest single application of lead worldwide is in lead–acid batteries. The

    most common type of lead–acid battery consists of a heavy duty plastic box (normally

    polypropylene) containing grids made from a lead–antimony alloy (commonly containing

    0.75–5% antimony) with minor additions of elements such as copper, arsenic, tin and

    selenium to improve grid properties. For the new generation of sealed, maintenance-free

    batteries, a range of lead–calcium–tin alloys is used. These contain up to 0.1% calcium and

    0–0.5% tin. The tin-containing alloys are used in the positive grids to protect against

    corrosion. Grids are still manufactured in pairs on special casting machines, but production

    of grids in strip form by continuous casting or expansion of rolled sheet is becoming

    increasingly popular as it facilitates automation and minimizes the handling of plates. The

    spaces in the grids are filled with a paste consisting largely of lead dioxide. When

    immersed in sulfuric acid, these pasted grids (plates) form an electric cell that generates

    electricity from the chemical reactions that take place. The reactions require the presence

    of lead dioxide and lead metal and each cell produces a voltage of 2V. These reactions are

    reversible and the battery can therefore be recharged. A rechargeable cell is known as a

    secondary cell and provides a means of storing electricity. Lead is well suited for this

    application because of its specific conductivity and its resistance to corrosion. The addition

    of antimony or calcium gives the lead an increased hardness to resist the mechanical

    stresses within the battery caused, for example, by the natural vibration of road vehicles

    and by the chemical reactions taking place (Lead Development Association International,

    2003e).

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  • The most common form of lead–acid battery is the so-called SLI battery (starting,

    lighting and ignition) used in road vehicles such as cars and trucks. Another form, the

    traction battery, is used to power vehicles such as golf carts and airport support vehicles.

    Other uses of lead power include larger stationary batteries for stand-by emergency power

    storage in hospitals and other critical facilities, and for some electricity utilities to help

    meet peak power demands and to maintain a stable electricity supply (Lead Development

    Association International, 2003e).

    INORGANIC AND ORGANIC LEAD COMPOUNDS 61

    Table 10. Trends in total industrial consumption of refined lead

    Consumption (thousand tonnes) by geographical regiona Year

    Ab B C Db E Fb Total

    1960 1152 19 986 204 65 654 3080

    1965 1306 33 1229 270 70 762 3670

    1970 1517 46 1488 360 72 1019 4502

    1975 1403 76 1454 413 86 1310 4742

    1980 1652 102 1476 600 85 1446 5361

    1985 1614 98 1510 735 69 1470 5496

    1990 2439 114 1648 1193 59 NRS 5454

    1995 1948 112 2017 1718 84 NRS 5879

    2000 2022 130 2332 1989 46 NRS 6519

    2003 2030 154 2012 2471 45 NRS 6712

    From International Lead and Zinc Study Group (1990, 2004)

    NRS, not reported separately a Data from the following countries:

    A, Austria, Belgium, Denmark, Finland, France, Germany (the Federal Republic of Germany

    before reunification), Greece, Ireland, Italy, Netherlands, Norway, Portugal, Spain, Sweden,

    Switzerland, United Kingdom and former Yugoslavia

    B, Algeria, Egypt, Morocco, South Africa, Tunisia and Zambia

    C, Argentina, Brazil, Canada, Mexico, Peru, USA and Venezuela

    D, India, Iran, Japan, Malaysia, Philippines, Republic of Korea, China (Province of Taiwan),

    Thailand and Turkey

    E, Australia and New Zealand

    F, Albania, Bulgaria, China, Cuba, former Czechoslovakia, Germany (the former German

    Democratic Republic), Hungary, People’s Democratic Republic of Korea; Poland, Romania,

    former Soviet Union; values for Albania, Cuba, China, Germany (the former German Democratic

    Republic), Peoples’ Democratic Republic of Korea, Romania and former Soviet Union are

    estimates. b From 1990 onwards, data from countries in region F are included in region A (Albania,

    Bulgaria, Czech Republic, Hungary, Poland, the former German Democratic Republic, Poland,

    Romania, Estonia, Latvia, Lithuania, Belarus, Russian Federation and Ukraine) or in region D

    (all other former Soviet Republics, China, Cuba and People’s Democratic Republic of Korea).

    Lead metal consumption for 1991 in the former Soviet Union was split as follows: Europe, 86%,

    Asia, 14%.

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  • Since 1960 the manufacture of lead–acid batteries has remained the largest single use

    of lead in nearly all countries, accounting for an ever-increasing percentage of total lead

    consumption (see Tables 12, 14 and 15) (International Lead and Zinc Study Group, 1992).

    IARC MONOGRAPHS VOLUME 8762

    Table 11. Total industrial lead consumption

    Consumption (thousand tonnes) in year Country or region

    1985 1990 1996 2001

    Australia 49.5 45.9 67.0 41.0

    Austria 58.0 65.5 58.0 59.0

    Belgium 66.8 67.7 50.6 40.3

    Brazil 79.6 75.0 110.0 112.0

    Canada 104.5 71.7 93.4 71.8

    China NA NA 470.1 700.0

    Czech Republic NA NA 25.0 80.0

    Finland 22.0 13.4 3.5 2.0

    Francea 234.3 261.6 273.8 282.5

    Germanya 348.2 375.3 331.0 392.6

    India 51.3 51.8 85.0 127.0

    Italya 235.0 259.0 268.0 283.0

    Japan 397.4 417.0 329.9 284.7

    Mexico 90.6 66.8 141.0 205.0

    Netherlands 45.1 65.0 57.0 30.0

    New Zealand 8.6 8.0 7.0 5.0

    Republic of Korea 81.0 150.0 289.8 314.7

    Romania NA NA 22.0 20.0

    Scandinaviab 55.6 36.3 49.0 13.0

    South Africa 48.2 65.9 63.1 59.1

    South-East Asiac 125.2 185.0 413.0 427.0

    Spain 125.3 126.7 144.0 246.0

    Switzerland 10.5 8.7 10.5 12.6

    United Kingdoma 303.2 334.0 309.2 266.5

    USAa 1148.3 1288.4 1554.4 1587.3

    Total 3688.2 4038.7 5225.3 5662.1

    From International Lead and Zinc Study Group (1992, 2003)

    NA, not available a Data for these countries include total metal usage in all forms, i.e. refined

    lead and alloys (lead content), plus re-melted lead recovered from secondary

    materials. Data for other countries include refined lead and alloys only. b Denmark, Norway and Sweden c China, Hong Kong Special Administrative Region, China (Province of

    Taiwan), Indonesia, Malaysia, Philippines and Singapore

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  • INORGANIC AND ORGANIC LEAD COMPOUNDS 63

    Table 12. Trends in uses of lead in selected countriesa

    Percentage of total usage in year Use

    1985 1990 1996 2001

    Batteries 57.7 63.0 72.5 76.7

    Cable sheathing 5.6 4.5 2.1 1.4

    Rolled and extruded productsb 7.6 7.7 5.9 6.0

    Shot/ammunition 2.8 2.8 2.3 2.1

    Alloys 4.2 3.3 3.2 2.5

    Pigments and other compounds 14.2 12.8 10.0 8.1

    Gasoline additives 3.7 2.1 0.9 0.4

    Miscellaneous 4.2 3.8 3.3 2.8

    Total 100.0 100.0 100.0 100.0

    From International Lead and Zinc Study Group (1992, 2003) a Countries include: Australia, Austria, Belgium, Brazil, Canada, China (Hong Kong

    Special Administrative Region), China (Province of Taiwan), Denmark, Finland, France,

    Germany, India, Indonesia, Italy, Japan, Malaysia, Mexico, Netherlands, New Zealand,

    Norway, Philippines, Republic of Korea, Singapore, South Africa, Spain, Sweden,

    Switzerland, United Kingdom and USA.

    b Including lead sheet

    Table 13. Trends in total lead consumption in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 196 240 233 262

    Germany 281 342 342 375

    Italy 108 259 280 259

    Japan 162 347 368 417

    United Kingdom 385 364 336 334

    USA 926 1398 1358 1288

    Total 2058 2950 2917 2935

    From International Lead and Zinc Study Group (1992)

    The data include refined metal and direct use of lead in scrap form.

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  • IARC MONOGRAPHS VOLUME 8764

    Table 14. Trends in principal uses of lead in six major consuming countries

    a

    Percentage of total use in year Use

    1960 1979 1990

    Batteries 27.7 50.8 64.4

    Cable sheathing 17.9 5.9 3.8

    Rolled/extruded products 18.0 7.7 7.8

    Shot/ammunition 3.2 3.2 3.8

    Alloys 10.5 6.7 3.5

    Pigment/compounds 9.9 12.3 10.9

    Gasoline additives 9.1 9.8 2.7

    Miscellaneous 3.7 3.6 3.1

    Total 100.0 100.0 100.0

    From International Lead and Zinc Study Group (1992) a France, Germany, Italy, Japan, United Kingdom and USA

    Table 15. Trends in consumption of lead for batteries in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 45.0 90.0 110.7 163.5

    Germanya 73.2 132.9 158.3 195.2

    Italy 25.5 68.0 93.0 113.2

    Japan 30.0 163.1 191.8 294.6

    United Kingdom 76.2 106.5 113.9 103.7

    USA 320.4 698.0 814.4 1019.6

    Total 570.3 1258.5 1481.2 1889.8

    From International Lead and Zinc Study Group (1992) a Excludes consumption by some independent producers of lead oxides

    for batteries.

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  • INORGANIC AND ORGANIC LEAD COMPOUNDS 65

    Table 16. Trends in consumption of lead for rolled/ extruded products in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 43.7 31.0 27.2 22.4

    Germany 44.3 31.1 32.7 39.1

    Italy 29.1 50.3 40.8 21.5

    Japan 35.9 39.6 26.7 10.9

    United Kingdom 88.0 57.7 48.9 98.6

    USA 130.1 90.2 47.7 35.8

    Total 371.1 299.9 224.0 228.3

    From International Lead and Zinc Study Group (1992)

    Table 17. Trend in consumption of lead for cable sheathing in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 60.8 41.1 21.4 16.3

    Germany 83.9 54.6 31.5 12.2

    Italy 24.0 44.8 40.0 48.7

    Japan 47.0 28.7 36.8 4.9

    United Kingdom 97.0 45.8 26.6 10.4

    USA 54.7 39.0 16.4 18.3

    Total 367.4 254.0 172.7 110.8

    From International Lead and Zinc Study Group (1992)

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  • IARC MONOGRAPHS VOLUME 8766

    Table 18. Trends in consumption of lead for alloys in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 17.3 14.8 9.3 3.2

    Germany 22.7 22.8 16.5 9.0

    Italy 6.0 6.0 5.7 3.5

    Japan 7.1 24.2 18.3 18.7

    United Kingdom 37.0 35.0 24.5 22.0

    USA 125.3 128.8 120.0 46.4

    Total 215.4 231.6 194.3 102.8

    From International Lead and Zinc Study Group (1992)

    Table 19. Trends in consumption of lead for pigments and compounds in six major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 11.9 34.5 33.0 29.4

    Germany 38.4 69.6 76.8 100.3

    Italy 10.1 45.2 60.4 40.0

    Japan 17.2 64.2 62.4 64.0

    United Kingdom 35.9 38.8 34.1 28.6

    USA 89.3 98.7 90.8 56.5

    Total 202.8 351.0 357.5 318.8

    From International Lead and Zinc Study Group (1992)

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  • 1.3.2 Lead sheet

    The use of lead sheet has increased dramatically over recent years, particularly for the

    building industry. Lead sheet has been produced for decades by traditional wide lead mills

    in which lead slabs are fed through large drum-like rollers, sometimes several times, to

    produce lead sheets of the desired thickness. The traditional wide lead mill is being

    replaced by more sophisticated rolling mills producing coils of lead 1.2–1.5 m wide. Most

    lead sheets in building applications are between 1.3 and 2.2 mm thick, but sheets of

    2.6–3.6 mm are used for roofing prestige buildings. Thick sheet alloys are rolled for

    applications such as anodes for electrowinning and thin foils are used for sound atte-

    nuation. A manufacturing technique other than milling is continuous casting in which a

    rotating, water-cooled drum is partly immersed in a bath of molten lead. The drum picks

    up a solid layer of lead, which is removed over a knife edge adjacent to the drum as it

    rotates. The thickness is controlled by varying the speed of rotation and the temperature of

    the drum (Lead Development Association International, 2003e).

    In the building industry, most of the lead sheet (or strip) is used as flashings or

    weatherings to prevent water from penetrating, the remainder being used for roofing and

    cladding. By virtue of its resistance to chemical corrosion, lead sheet is also used for the

    lining of chemical treatment baths, acid plants and storage vessels. The high density of

    lead sheet and its ‘limpness’ make it a very effective material for reducing the trans-

    mission of sound through partitions and doors of comparatively lightweight construction.

    Often the lead sheet is bonded adhesively to plywood or to other building boards for con-

    venience of handling. A particular advantage of the high density of lead is that only rela-

    tively thin layers are needed to suppress the transmission of sound (Lead Development

    Association International, 2003e).

    Lead sheet is the principal element in the product category ‘rolled and extruded

    products’. In many countries, the demand for rolled and extruded lead products declined

    in the 1960s and 1970s, due in part to a rapid decline in the use of lead pipe (see Tables

    14 and 16). Nevertheless, in a number of countries (see Table 12), lead sheet remains the

    third largest use of lead at about 6% of the total reported consumption (International Lead

    and Zinc Study Group, 1992, 2003).

    1.3.3 Lead pipes

    Lead piping, once a substantial use in the ‘rolled and extruded products’ category, has

    been replaced progressively by copper tubes for the transport of domestic water and the

    supply of gas and by plastic tubing for disposal of wastewater. Lead pipes have not been

    used in new supplies of domestic water for about 30 years. However, due to their

    corrosion-resistant properties, they are still used for transport of corrosive chemicals at

    chemical plants. Also, lead pipe of appropriate composition is extruded for cutting into

    short-length ‘sleeves’ used in the jointing of lead-sheathed cables (see below) (Inter-

    national Lead and Zinc Study, 1992; Lead Development Association International, 2003e).

    INORGANIC AND ORGANIC LEAD COMPOUNDS 67

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  • 1.3.4 Cable sheathing

    Because of its corrosion resistance when in contact with a wide range of industrial and

    marine environments, soils and chemicals, lead was one of the first materials to be used to

    provide an impervious sheath on electric cables. Lead can be applied to the cable core in

    unlimited lengths by extrusion at temperatures that do not damage the most sensitive

    conductors (optical fibres) or insulating materials (paper or plastics). Lead is pliable and

    withstands the coiling, uncoiling, handling and bending operations involved in the

    manufacturing and installation of the cable. A lead sheath can be readily soldered at low

    temperatures when cables need to be jointed or new cables installed. With modern screw-

    type continuous extruders, unjointed submarine power cables as long as 100 km have been

    produced (Lead Development Association International, 2003e).

    Until 1960 sheathing of electrical cables was the largest single use of lead in many

    countries including France, Germany, Japan and the United Kingdom, representing

    25–30% of total lead consumption in these four countries. It was used much less exten-

    sively in the USA where, during the late 1950s, lead was replaced by alternative materials,

    generally plastics, as the sheathing material for telephone cables. Since the mid-1960s,

    however, there has been a gradual decline in the use of lead for cable sheathing in most

    countries (Table 17). By 1990, lead consumption for cable sheathing had fallen to 4.5%

    of total consumption and, by 2001, to 1.4% (Table 12) (International Lead and Zinc Study

    Group, 1992, 2003).

    1.3.5 Lead alloys

    (a) Lead–antimony alloysBy far the largest use of lead–antimony alloys is in batteries. At one time, antimony

    contents of ∼10% were common, but the current generation of lead–acid batteries has amuch lower antimony content. Alloys with 1–12% antimony are used widely in the

    chemical industry for pumps and valves, and in radiation shielding both for lining the

    walls of X-ray rooms and for bricks to house radioactive sources in the nuclear industry.

    The addition of antimony to lead increases the hardness of the lead, and therefore its resis-

    tance to physical damage, without greatly reducing its corrosion resistance (Lead Deve-

    lopment Association International, 2003e).

    (b) SoldersSoldering is a method of joining materials, in which a special metal (solder) is applied

    in the molten state to wet two solid surfaces and join them on solidification. Solders are

    classified according to their working temperatures. Soft solders, which have the lowest

    melting-points, are largely lead–tin alloys with or without antimony, while fusible alloys

    contain various combinations of lead, tin, bismuth, cadmium and other low melting-point

    metals. Depending on the application, lead–tin solders may contain from a few per cent

    to more than 60% tin.

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  • A substantial proportion of solder is used in electrical or electronic assemblies. The

    advances made in the electronics industry have required the development of fast and

    highly-automated methods of soldering. Printed circuit assemblies can be soldered by

    passing them across a standing wave of continuously-circulating molten solder (Lead

    Development Association International, 2003e).

    The use of lead solder in plumbing has declined with the replacement of lead piping

    by copper tubing and, more recently, as a result of concerns of potential leaching of lead

    into water supplies. Similarly, concerns of possible danger to health have restricted the

    use of lead solders in the canning industry, formerly an important market.

    (c) Lead for radiation shieldingLead and its alloys in metallic form, and lead compounds, are used in various forms

    of radiation shielding. The shielding of containers for radioactive materials is usually

    metallic lead (see above). Radioactive materials in laboratories and hospitals are usually

    handled by remote control from a position of safety behind a wall of lead bricks. X-ray

    machines are normally installed in rooms lined with lead sheet; lead compounds are

    constituents of the glass used in shielding partitions to permit safe viewing; and lead

    powder is incorporated into plastic and rubber sheeting materials used for protective

    clothing (Lead Development Association International, 2003e).

    (d) Other uses of lead alloysA variety of lead alloys are produced for a wide range of applications in various

    industries. In the 1990s, these alloys accounted for 130–150 000 tonnes of lead used in

    industrialized countries (Table 18). However, the trend in this sector had been one of steady

    decline during the previous three decades (Table 14), as some uses have been overtaken by

    technological changes or have been restricted by health and environmental regulations.

    The use of terne metal (a thin tin–lead alloy coating) for corrosion protection, and the

    addition of lead to brass and bronze to assist in free machining, and in bearing metals to

    reduce friction and wear in machinery, have declined slowly due to competition from alter-

    native materials such as aluminum and plastics. The market for type metal in the printing

    industry has largely disappeared as hot metal printing has been replaced by new techno-

    logy. In the USA, this use peaked at 30 000 tonnes in 1965 but had fallen to 1–2000 tonnes

    by the mid-1980s and is similarly low in other developed countries (International Lead and

    Zinc Study Group, 1992).

    1.3.6 Lead pigments and compounds

    The market for lead pigments and compounds constitutes the second largest use of lead

    after lead–acid batteries. The market peaked in the mid-1980s, when over 500 000 tonnes

    of lead were used in lead pigments and compounds, mainly by the plastics, glass and

    ceramics industries, and accounting for 14% of total lead consumption (Table 14). Since

    INORGANIC AND ORGANIC LEAD COMPOUNDS 69

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  • then these uses have been restricted by health and environmental concerns while still

    remaining the second largest use of lead (8% of total lead consumption) (Table 12).

    Besides the six major consuming countries (Table 19), pigments and compounds are

    also the second most important use of lead in other countries including Brazil, Canada, the

    Republic of Korea, South Africa, Spain and countries of South-East Asia (International

    Lead and Zinc Study Group, 1992, 2003).

    (a) Lead pigmentsThe use of lead in paints for domestic purposes and in some commercial and industrial

    applications is now severely restricted or banned in view of the potential health risks

    caused by exposure to weathered or flaking paint. However, lead tetraoxide (Pb3O4) still

    retains some of its traditional importance for rust-inhibiting priming paints applied directly

    to iron and steel in view of its anti-corrosion properties, but faces growing competition

    from zinc-rich paints containing zinc dust and zinc chromate. The use of lead carbonate

    (white lead) in decorative paints has been phased out. Calcium plumbate-based paints are

    effective on galvanized steel. Lead chromate (yellow) and lead molybdate (red orange) are

    still used in plastics and to a lesser extent in paints. Lead chromate is used extensively as

    the yellow pigment in road markings and signs, which are now commonplace in most

    European countries and in North America (Lead Development Association International,

    2003e).

    (b) Lead stabilizers for polyvinyl chloride (PVC)Lead compounds are used in both rigid and plasticized PVC to extend the temperature

    range at which PVC can be processed without degradation. In the building industry, the

    widespread adoption of PVC materials for corrosion-resistant piping and guttering in

    industrial facilities, for potable water piping (lead content, < 1%), and for windows and

    door frames provides a major market for lead sulfate and lead carbonate as stabilizers to

    prevent degrading of PVC during processing and when exposed to ultraviolet light.

    However, concerns over potential health hazards are limiting the use of lead in PVC water

    piping in some countries. Dibasic lead phosphite also has the property of protecting

    materials from degradation by ultraviolet light. Normal and dibasic lead stearates are

    incorporated as lubricants. All these compounds are white pigments that cannot be used

    when clear or translucent articles are required (International Lead and Zinc Study Group,

    1992; Lead Development Association International, 2003e). The levels of lead in 16

    different PVC pipes used for water supplies in Bangladesh were found to be in the range

    of 1.1–6.5 mg/g (Hadi et al., 1996).

    (c) Lead in glassDecorative lead crystal glass was developed in England in the seventeenth century.

    Normally added in the form of lead monoxide (PbO) at 24–36%, lead adds lustre, density

    and brilliance to the glass. Its attractiveness is further enhanced by decorative patterns that

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  • can be cut on the surface and by the characteristic ring associated with lead crystal. There

    is now a substantial market for a cheaper form of ‘semi-crystal’ containing 14–24% lead

    oxide, and such glasses are usually moulded with the decorative pattern rather than being

    hand-cut later. Lead is also used in optical glass (e.g. telescopes, binoculars), ophthalmic

    glass (e.g. spectacles), electrical glass (e.g. lamp tubing, cathode ray tubes) and radiation

    protection glass (e.g. for windows in remote-handling boxes, television tubes) (Lead

    Development Association International, 2003e).

    (d) Lead for ceramicsLead is used in a wide range of glaze formulations for items such as tableware

    (earthenware and china), wall and floor tiles, porcelain and sanitary-ware and electrical

    transistors and transducers. The lead compounds used are mainly lead monoxide (litharge,

    PbO), lead tetraoxide and lead silicates. The properties offered by lead compounds are

    low melting-points and wide softening ranges, low surface tension, good electrical

    properties and a hard-wearing and impervious finish. Lead compounds are also used in

    the formulation of enamels used on metals and glass.

    Another important application for lead compounds is in a range of ceramics (other than

    the glazes) used in the electronics industry. Typical of these are piezoelectric materials such

    as the lead zirconate/lead titanate range of compositions known generally as PZI. These

    materials have a wide range of applications, such as spark generators, sensors, electrical

    filters, gramophone pick-ups and sound generators (International Lead and Zinc Study

    Group, 1992; Lead Development Association International, 2003e).

    1.3.7 Gasoline additives

    Tetraethyl and tetramethyl lead have been used as anti-knock additives in gasoline, at

    concentrations up to 0.84 g/L, as an economic method of raising the ‘octane rating’ to

    provide the grade of gasoline needed for the efficient operation of internal combustion

    engines of high compression ratio (Thomas et al., 1999). However, increasing recognitionof the potential health effects from exposure to lead has led to the reformulation of gasoline

    and the removal of lead additives. In addition, lead in gasoline is incompatible with the

    catalytic converters used in modern cars to control nitrogen oxides, hydrocarbons and other

    ‘smog’-producing agents. The use of lead in gasoline in the USA has been phased out

    gradually since the mid-1970s, and moves to phase it out in the European Community

    began in the early 1980s. Since 1977 in the USA and 1991 in Europe, all new cars are

    required to run on unleaded gasoline. By the end of 1999, forty countries or regions had

    banned the use of lead in gasoline (Table 20), although it is still permitted in some of these

    countries for certain off-road and marine vehicles and for general aviation aircraft (Smith,

    2002). Numerous other countries are planning the phase-out of lead in gasoline in the near

    future. About 79% of all gasoline sold in the world in the late 1990s was unleaded

    (International Lead Management Center, 1999). The market for tetraethyl and tetramethyl

    lead has declined considerably (Table 21) and will continue to do so (Lead Development

    INORGANIC AND ORGANIC LEAD COMPOUNDS 71

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  • Association International, 2003e). In 2001, less than 0.5% of lead consumption was for

    gasoline additives (Table 12) (International Lead and Zinc Study Group, 2003).

    1.3.8 Miscellaneous uses

    About 150 000 tonnes of lead are employed each year in a variety of other uses, of

    which about 100 000 tonnes are consumed in the production of lead shot and ammunition

    in the major consuming countries (excluding Japan where this use is not reported

    IARC MONOGRAPHS VOLUME 8772

    Table 20. Countries or regions that had phased out the use of lead in gasoline

    a by the end of 1999

    Argentina

    Austria

    Bahamas

    Bangladesh

    Belize

    Bermuda

    Bolivia

    Brazil

    Canada

    Colombia

    Costa Rica

    Denmark

    Dominican Republic

    El Salvador

    Finland

    Germany

    Guam

    Guatemala

    Haiti

    Honduras

    Hong Kong SAR

    Hungary

    Iceland

    Japan

    Luxembourg

    Malaysia

    Mexico

    Netherlands

    New Zealand

    Nicaragua

    Norway

    Portugal

    Puerto Rico

    Republic of Korea

    Singapore

    Slovakia

    Sweden

    Thailand

    USA

    US Virgin Islands

    From International Lead Management Center (1999) a See Section 1.3.7 for permitted uses of leaded gasoline.

    Table 21. Trends in consumption of lead for gasoline additives in five major consuming countries

    Consumption (thousand tonnes) in year Country

    1960 1973 1979 1990

    France 6.1 13.5 15.1 9.8

    Germany NA 9.4 10.8 NA

    Italy 4.8 11.8 13.0 3.7

    United Kingdom 27.1 54.4 58.9 45.1

    USA 148.6 248.9 186.9 20.7

    Total 186.6 338.0 284.7 79.3

    From International Lead and Zinc Study Group (1992)

    NA, not available

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  • separately). Globally, this use has remained relatively stable since the 1960s, at around

    3–4% of total lead consumption (Tables 12 and 14).

    Lead cames have long been a feature of stained-glass windows in churches and

    cathedrals. They consist of H-shaped sections of lead which hold together the individual

    pieces of glass. They are now being used more widely in modern homes both in the tradi-

    tional way and in the form of self-adhesive strips stuck on to a larger piece of glass to

    simulate an integral came.

    Lead weights for fishing have been largely phased out but lead stampings, pressings

    and castings are widely used for many weighting applications, for example curtain

    weights, wheel balance weights, weights for analytical instruments and yacht keels.

    Lead wool is made by scratching fine strands from the surface of a lead disc. It is used

    for the caulking of joints in large pipes like gas mains and in some specialty batteries.

    Lead-clad steel is a composite material manufactured by cold rolling lead sheet onto

    sheet steel that has been pretreated with a terne plate. A strong metallurgical bond is

    formed between the lead and the steel, which provides a material that combines the

    physical and chemical properties of lead with the mechanical properties of steel. Although

    primarily aimed at the sound-insulation market, lead-clad steel has also found use in

    radiation shielding and in the cladding of buildings.

    Lead powder is incorporated into a plasticizer to form sheets of lead-loaded plastic.

    This material is used to make radiation-protective clothing and aprons for the medical,

    scientific and nuclear industries (see Section 1.4.5.c). It also has sound-insulating

    properties. Lead powder is also used as the basis for some corrosion-resistant paints (see

    Section 1.4.6).

    Smaller amounts of lead are used in galvanizing, annealing and plating (International

    Lead and Zinc Study Group, 1992; Lead Development Association International, 2003e).

    1.4 Occurrence

    1.4.1 Environmental occurrence

    Lead was one of the first metals used by man; there is evidence that it has been used

    for approximately 6000 years (Hunter, 1978). As a result, although both natural and anthro-

    pogenic processes are responsible for the distribution of lead throughout the environment,

    anthropogenic releases of lead are predominant. Industrial releases to soil from nonferrous

    smelters, battery plants, chemical plants, and disturbance of older structures containing

    lead-based paints are major contributors to total lead releases. Lead is transferred conti-

    nuously between air, water, and soil by natural chemical and physical processes such as

    weathering, run-off, precipitation, dry deposition of dust, and stream/river flow; however,

    soil and sediments appear to be important sinks for lead. Lead is extremely persistent in

    both water and soil. Direct application of lead-contaminated sludge as fertilizers, and

    residues of lead arsenate used in agriculture, can also lead to the contamination of soil,

    sediments, surface water and ground water. In countries where leaded gasoline is still used,

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  • the major air emission of lead is from mobile and stationary sources of combustion.

    Besides environmental exposures, exposure to lead may arise from sources such as foods

    or beverages stored, cooked or served in lead-containing containers, food growing on

    contaminated soils, and traditional remedies, cosmetics and other lead-containing products.

    The ubiquity of lead in the environment has resulted in present-day body burdens that

    are estimated to be 1000 times those found in humans uncontaminated by anthropogenic

    lead uses (Patterson et al., 1991), but exposures have decreased substantially over the past10–30 years in countries where control measures have been implemented.

    The estimated contributions of the common sources and routes of lead exposure to total

    lead intake vary from country to country and over time. In 1990, the estimated daily intake

    of lead from consumption of food, water and beverages in the USA ranged from 2 to

    9 µg/day for various age groups and was approximately 4 µg/day for children 2 years ofage and younger (ATSDR, 1999). For many young children, the most important source of

    lead exposure is through ingestion of paint chips and leaded dusts and soils released from

    ageing painted surfaces or during renovation and remodeling (CDC, 1997a; Lanphear

    et al., 1998). Compared with nonsmokers, smokers have an additional lead intake ofapproximately 6 µg/day, based on an estimated exposure of 14 µg/day and absorption of30